JPH111385A - Composing unused resource - Google Patents
Composing unused resourceInfo
- Publication number
- JPH111385A JPH111385A JP18711097A JP18711097A JPH111385A JP H111385 A JPH111385 A JP H111385A JP 18711097 A JP18711097 A JP 18711097A JP 18711097 A JP18711097 A JP 18711097A JP H111385 A JPH111385 A JP H111385A
- Authority
- JP
- Japan
- Prior art keywords
- conditioner
- fermentation
- organic substance
- agricultural
- solid organic
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
- Y02A40/20—Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/40—Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/78—Recycling of wood or furniture waste
Abstract
Description
【0001】[0001]
【発明の属する技術】この発明は、農水畜産加工場や家
庭からの廃棄物を腐敗させることなく多量にまた短時間
に種菌を用い少量のエネルギーで効率よく発酵させ堆肥
化し、農業や園芸用などの高効果土壌肥料として土に還
元し利用する堆肥化方法に関するものである。The present invention relates to agriculture, horticulture, and the like, in which fertilizer is efficiently fermented with a small amount of energy using a large amount of inoculum in a short time without spoiling wastes from agricultural, marine and livestock processing plants and households. The present invention relates to a composting method for reducing and using soil as a highly effective soil fertilizer.
【0002】[0002]
【従来の技術】従来、農水畜産廃棄物などを発酵処理す
るためには、それらの水分の含有量が高いため、脱水処
理または多量のオガクズやモミガラなどの副材料を加え
て発酵に適した条件に水分調整をしなければならなかっ
た。2. Description of the Related Art Conventionally, fermentation treatment of agricultural, aquatic and livestock wastes has been carried out under conditions suitable for fermentation by dehydration treatment or addition of a large amount of auxiliary materials such as sawdust and peaches due to their high water content. I had to adjust the water.
【0003】また、寒冷期には、廃棄物そのものが低温
であるため発酵が始まらず加温装置により加温しなけれ
ばならなかった。従って、発酵処理するためには、多量
のエネルギーや設備のコストが必要となりまた種菌の発
酵条件が安定せず効率が悪く、その結果薬品処理や焼却
などにより無駄なコストをかけて廃棄処分されていた。[0003] In the cold season, since the waste itself is at a low temperature, fermentation does not start and the waste must be heated by a heating device. Therefore, fermentation requires a large amount of energy and equipment costs, and the fermentation conditions of the inoculum are not stable, resulting in poor efficiency. As a result, wastes are discarded at a wasteful cost due to chemical treatment or incineration. Was.
【0004】また従来の方法によると一回の発酵のみで
堆肥化されるためリン酸、カリをはじめ微量土壌成分等
高度な肥料成分が濃縮されなかったが、この考案により
循環されることによりそれらの成分を固形有機物等効果
的に濃縮できることとなった。Further, according to the conventional method, composting is performed only by one fermentation, so that high-grade fertilizer components such as phosphoric acid and potassium, as well as trace soil components, were not concentrated. Can be effectively concentrated such as solid organic matter.
【0005】[0005]
【発明が解決しようとする課題】農水畜産廃棄物の発酵
処理は、水分調整するための脱水装置またはオガクズや
モミガラなどの多量の調整副材料が必要であった。The fermentation treatment of agricultural, livestock, and livestock waste requires a dehydrator for adjusting the water content or a large amount of auxiliary materials such as sawdust and peach.
【0006】また、寒冷期には発酵開始時の温度調整の
ための加温設備が必要となり処理に高い設備とエネルギ
ーコストが必要となり採算ベースに合わず困難であっ
た。[0006] In the cold season, a heating facility for adjusting the temperature at the start of fermentation is required, which requires a high facility and energy cost for the treatment, which is difficult to meet the profitable base.
【0007】[0007]
【課題を解決するための手段】一度発酵処理のための水
分調整材として使用し発酵させた混入材のウッドチップ
やバーク材などの多孔質な固形有機物等を、発酵直後に
ふるいにかけ選別し再度水分調整副材料としてまた熱量
運搬のための加温材として新しい廃棄物の中に混入し循
環させて使用することにより省エネルギー、低コストで
効率の高い発酵処理を可能にし、しかも有効肥料成分の
高い堆肥を得ることが可能となった。[Means for Solving the Problems] Porous solid organic matter, such as wood chips and bark wood, which have been fermented once and used as a water conditioner for fermentation, are sieved immediately after fermentation and re-selected. By mixing and circulating it in new waste as a moisture control auxiliary material and as a heating material for transporting heat, it can be used for energy saving, low cost and efficient fermentation, and high effective fertilizer components It became possible to obtain compost.
【0008】[0008]
【発明の実施の形態】発明の実施の形態を実施例にもと
づき図面を参照して説明する。実施例は、堆肥化するた
めに発酵処理を一次発酵と二次発酵に分けた。図1は、
一次発酵槽1に破砕された農水畜産廃棄物である発酵性
有機物と家畜糞及びウッドチップを混合させた培地2を
収納する。DESCRIPTION OF THE PREFERRED EMBODIMENTS Embodiments of the present invention will be described based on embodiments with reference to the drawings. In the examples, the fermentation treatment was divided into primary fermentation and secondary fermentation for composting. FIG.
A primary fermenter 1 contains a culture medium 2 in which crushed fermentable organic matter, which is crushed agricultural and livestock waste, livestock dung and wood chips are mixed.
【0009】一次発酵槽1内の培地2の水分は、50〜
60%に調整しておけば効率を高めることができる。ま
た、培地2の温度は、最低でも摂氏15度に調整する。The water content of the culture medium 2 in the primary fermenter 1 is 50 to
Adjusting to 60% can increase the efficiency. The temperature of the culture medium 2 is adjusted to at least 15 degrees Celsius.
【0010】ウッドチップなどの多孔質な固形有機物等
は、培地2内の空気の均一な供給、水分調整、温度調
整、種菌の繁殖肥効成分の濃縮などを目的として加えら
れているが、本考案では一次発酵に繰り返し選別して使
用するので固形容積は、2.0〜3.0立方センチメー
トル程度が適当である。[0010] Porous solid organic substances such as wood chips are added for the purpose of uniformly supplying air in the culture medium 2, adjusting the water content, adjusting the temperature, and concentrating the fertilizing components for the propagation of the inoculum. In the present invention, since it is repeatedly selected and used for the primary fermentation, the solid volume is suitably about 2.0 to 3.0 cubic centimeters.
【0011】外気からブロアー4により湿度の低い新鮮
な空気を培地2全体に均一に行き渡るように送気吹出管
3へ送る。[0011] Fresh air having a low humidity is blown from the outside air by a blower 4 to the air blow-out pipe 3 so as to uniformly spread over the entire culture medium 2.
【0012】培地2内に5〜7日間送気及び切替し(混
合)を続けると微生物が好気性の高温発酵(一次発酵)
する。この時の発酵温度は約摂氏65〜70度である。When air is supplied and switched (mixed) into the medium 2 for 5 to 7 days, the microorganisms undergo aerobic high-temperature fermentation (primary fermentation).
I do. The fermentation temperature at this time is about 65 to 70 degrees Celsius.
【0013】次に、一次発酵槽1から培地2の一次発酵
体を選別ふるい装置5にかける。ふるいを通過し充分空
気を吸収した発酵体は、二次発酵槽9に収納する。Next, the primary fermentation medium 2 from the primary fermentation tank 1 is passed through a sorting and sieving apparatus 5. The fermented body that has passed through the sieve and has sufficiently absorbed air is stored in the secondary fermenter 9.
【0014】外気からブロアー10により湿度の低い新
鮮な空気を培地8全体に均一に行き渡るように送気吹出
管11へ送る。[0014] Fresh air having a low humidity is sent from the outside air to the air blow-off pipe 11 by the blower 10 so as to uniformly spread the whole medium 8.
【0015】二次発酵槽9内の培地8で送気及び切替し
(混合)を続けると、約摂氏45〜55度で堆肥化熟成
発酵(二次発酵)が始まり30〜90日間続いた後微生
物の発酵発熱がおさまる。この時点で堆肥化が完了とな
り土壌還元が可能となる。When air supply and switching (mixing) are continued in the medium 8 in the secondary fermentation tank 9, compost maturation fermentation (secondary fermentation) starts at about 45 to 55 degrees Celsius and continues for 30 to 90 days. The fermentation fever of the microorganism subsides. At this point, composting is complete and soil can be reduced.
【0016】一方、一次発酵終了後、選別ふるい装置5
のふるいを通過しなかったウッドチップなどの多孔質な
固形有機物等は、断熱された調整材槽6に分別され収納
する。On the other hand, after the completion of the primary fermentation, the screening device 5
Porous solid organic matter such as wood chips that have not passed through the sieve are separated and stored in an insulated adjusting material tank 6.
【0017】調整材7は、発酵直後であるため摂氏50
〜60度の高温であり高い熱エネルギーを保持し、ま
た、一次発酵で水分は約40〜50%まで減少してい
る。従って、一次発酵に必要な種菌としての機能の他
に、十分な熱量の運搬による加温及び水分調整材として
の機能を持ち備えている。The conditioning material 7 is 50 degrees Celsius immediately after fermentation.
It has a high temperature of 6060 degrees and retains high thermal energy, and the primary fermentation has reduced the water content to about 40-50%. Therefore, in addition to the function as a seed fungus necessary for primary fermentation, it has a function as a heating and moisture adjusting material by transporting a sufficient amount of heat.
【0018】調整材7は、繰り返し循環して新たな農水
畜産廃棄物の発酵処理調整材として混入して使用する。
尚、この調整材7は、有機物である場合は発酵微生物に
より分解されるため古いものは肥効成分を濃縮した上で
堆肥化される。不足分は培地2へ新しいウッドチップを
常に補給し混入させるもである。固形有機物代替品の場
合には濃縮された肥効成分を水等で抽出した上で再度使
用される。The conditioning material 7 is repeatedly circulated and used as a fresh fermentation treatment conditioning material for agricultural, aquatic and livestock waste.
When the adjusting material 7 is an organic substance, it is decomposed by fermentation microorganisms, so that the old material is composted after concentrating fertilizing components. The shortage is to constantly replenish and mix new wood chips into the medium 2. In the case of a solid organic matter substitute, the concentrated fertilizer is extracted again with water or the like, and then used again.
【0019】[0019]
【発明の効果】水産加工場などからの廃棄物は、冬期間
摂氏5度以下のものを多く投入されるため、培地2全体
の温度が低下し一次発酵が困難になる。ここで調整材7
を投入し混合させるため、調整材そのものが持っている
熱量によって培地2全体の温度を摂氏15度以上に上昇
させることになる。従って、石油ボイラーなど大量のエ
ネルギーによる加温の必要性がなくなる。As described above, since a large amount of waste from a fishery processing plant or the like is introduced during the winter, the temperature of the whole culture medium 2 is lowered and primary fermentation becomes difficult. Here the adjusting material 7
Is added and mixed, the temperature of the entire culture medium 2 is raised to 15 degrees Celsius or more by the amount of heat of the adjusting material itself. Therefore, the necessity of heating by a large amount of energy such as an oil boiler is eliminated.
【0020】農水畜産廃棄物の水分は80〜100%と
非常に高くその分離は極めて難しい。水分の低い調整材
7を投入し配合することにより水分を吸い取り均一化し
た適度の水分値まで低下させることができる。尚、この
水分調整には必要に応じて新しく補給されたウッドチッ
プ等も混入させるものである。The water content of agricultural, livestock, and livestock wastes is extremely high at 80 to 100%, and its separation is extremely difficult. By adding and blending the adjusting material 7 having a low moisture content, the moisture content can be reduced to a uniform and moderate moisture value. In addition, in this moisture adjustment, wood chips and the like newly replenished are mixed if necessary.
【0021】これらの機能及び働きと同時に、固形有機
物等は種菌の均一配合及び造粒化による送気の均一供給
の役目も同時に果たすものであり高い効率の発酵を促進
できる。At the same time as these functions and functions, the solid organic matter and the like also play a role of uniform blending of the inoculum and uniform supply of air supply by granulation, and can promote highly efficient fermentation.
【図1】一次発酵槽の説明断面図である。FIG. 1 is an explanatory sectional view of a primary fermenter.
【図2】選別ふるい装置及び二次発酵槽の説明断面図で
ある。FIG. 2 is an explanatory sectional view of a sorting and sieving apparatus and a secondary fermenter.
1 一次発酵槽 2、 8 培地 3、11 送気吹出管 4、10 ブロワー 5 選別ふるい装置 6 調整材槽 7 調整材 9 二次発酵槽 DESCRIPTION OF SYMBOLS 1 Primary fermentation tank 2, 8 Culture medium 3, 11 Air blow-off pipe 4, 10 Blower 5 Sorting and sieving apparatus 6 Adjustment material tank 7 Adjustment material 9 Secondary fermentation tank
Claims (1)
畜糞尿とウッドチップやバークなどの多孔質な固形有機
物またはその人工的代替物(以下固形有機物等と呼ぶ)
を繰り返し循環させながら混入させることにより、種菌
供給・水分調整及び温度調整し肥料分を濃縮させながら
発酵処理させることを特徴とする堆肥化方法。1. Fermentable organic substances such as agricultural and livestock wastes and livestock manure and porous solid organic substances such as wood chips and bark or artificial substitutes thereof (hereinafter referred to as solid organic substances).
A method of composting, characterized in that fermentation is carried out while concentrating fertilizer by controlling the supply of seed bacteria, adjusting the water content and adjusting the temperature by mixing and recirculating the mixture.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP18711097A JPH111385A (en) | 1997-06-10 | 1997-06-10 | Composing unused resource |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP18711097A JPH111385A (en) | 1997-06-10 | 1997-06-10 | Composing unused resource |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH111385A true JPH111385A (en) | 1999-01-06 |
Family
ID=16200284
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP18711097A Pending JPH111385A (en) | 1997-06-10 | 1997-06-10 | Composing unused resource |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH111385A (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2001122684A (en) * | 1999-10-20 | 2001-05-08 | Bankei Recycle Center:Kk | Method for resource recovery treatment of shell to agricultural soil calcium makeup material |
KR100348637B1 (en) * | 1999-07-21 | 2002-08-13 | 김재인 | Witout Discharging Treatment System and Paddy Rice Fertilizer by The Composting Method of Livestock Sewage. |
KR100369237B1 (en) * | 2000-09-14 | 2003-01-24 | 김원중 | Method for treating a food waste and livestock wastes at the same time |
CN107030092A (en) * | 2017-04-26 | 2017-08-11 | 广西升禾环保科技股份有限公司 | A kind of garbage classification processing unit |
-
1997
- 1997-06-10 JP JP18711097A patent/JPH111385A/en active Pending
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR100348637B1 (en) * | 1999-07-21 | 2002-08-13 | 김재인 | Witout Discharging Treatment System and Paddy Rice Fertilizer by The Composting Method of Livestock Sewage. |
JP2001122684A (en) * | 1999-10-20 | 2001-05-08 | Bankei Recycle Center:Kk | Method for resource recovery treatment of shell to agricultural soil calcium makeup material |
JP4490529B2 (en) * | 1999-10-20 | 2010-06-30 | 株式会社ばんけいリサイクルセンタ− | Recycling method of shellfish to soil calcium supplement for agriculture |
KR100369237B1 (en) * | 2000-09-14 | 2003-01-24 | 김원중 | Method for treating a food waste and livestock wastes at the same time |
CN107030092A (en) * | 2017-04-26 | 2017-08-11 | 广西升禾环保科技股份有限公司 | A kind of garbage classification processing unit |
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